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WO2012034902A1 - Catalyst for the decomposition of nitrogen protoxide - Google Patents

Catalyst for the decomposition of nitrogen protoxide Download PDF

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Publication number
WO2012034902A1
WO2012034902A1 PCT/EP2011/065393 EP2011065393W WO2012034902A1 WO 2012034902 A1 WO2012034902 A1 WO 2012034902A1 EP 2011065393 W EP2011065393 W EP 2011065393W WO 2012034902 A1 WO2012034902 A1 WO 2012034902A1
Authority
WO
WIPO (PCT)
Prior art keywords
catalyst
rare earth
catalyst according
oxide
nitrogen protoxide
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Ceased
Application number
PCT/EP2011/065393
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English (en)
French (fr)
Inventor
Alberto Cremona
Marvin Estenfelder
Edoardo Vogna
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Sued Chemie Catalysts Italia SRL
Original Assignee
Sued Chemie Catalysts Italia SRL
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Sued Chemie Catalysts Italia SRL filed Critical Sued Chemie Catalysts Italia SRL
Priority to US13/822,880 priority Critical patent/US8809224B2/en
Priority to RU2013116992/05A priority patent/RU2573000C2/ru
Priority to ES11752239.1T priority patent/ES2666214T3/es
Priority to EP11752239.1A priority patent/EP2616165B1/en
Priority to PL11752239T priority patent/PL2616165T3/pl
Priority to KR1020137009320A priority patent/KR101882959B1/ko
Priority to CN201180044013.3A priority patent/CN103249468B/zh
Priority to CA2812142A priority patent/CA2812142C/en
Priority to NO11752239A priority patent/NO2616165T3/no
Publication of WO2012034902A1 publication Critical patent/WO2012034902A1/en
Anticipated expiration legal-status Critical
Ceased legal-status Critical Current

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Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8621Removing nitrogen compounds
    • B01D53/8625Nitrogen oxides
    • B01D53/8628Processes characterised by a specific catalyst
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/84Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/889Manganese, technetium or rhenium
    • B01J23/8892Manganese
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/54Nitrogen compounds
    • B01D53/56Nitrogen oxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/84Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/889Manganese, technetium or rhenium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/61Surface area
    • B01J35/615100-500 m2/g
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/02Impregnation, coating or precipitation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/024Multiple impregnation or coating
    • B01J37/0242Coating followed by impregnation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/024Multiple impregnation or coating
    • B01J37/0244Coatings comprising several layers
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/206Rare earth metals
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/207Transition metals
    • B01D2255/2073Manganese
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2255/00Catalysts
    • B01D2255/20Metals or compounds thereof
    • B01D2255/207Transition metals
    • B01D2255/20746Cobalt
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/40Nitrogen compounds
    • B01D2257/402Dinitrogen oxide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J21/00Catalysts comprising the elements, oxides, or hydroxides of magnesium, boron, aluminium, carbon, silicon, titanium, zirconium, or hafnium
    • B01J21/02Boron or aluminium; Oxides or hydroxides thereof
    • B01J21/04Alumina
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/50Catalysts, in general, characterised by their form or physical properties characterised by their shape or configuration
    • B01J35/55Cylinders or rings
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/10Capture or disposal of greenhouse gases of nitrous oxide (N2O)
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/30Improvements relating to adipic acid or caprolactam production

Definitions

  • the present invention relates to a catalyst for the catalytic decomposition of nitrogen protoxide (N 2 0) to nitrogen and oxygen, and to its use for the removal of the protoxide from gas mixtures which contain it, particularly for removing the emissions of nitric acid and adipic acid plants.
  • N 2 0 nitrogen protoxide
  • Nitrogen protoxide is a harmful greenhouse gas that is much more powerful than carbon dioxide; moreover, in the stratosphere it takes part in the reactions that lead to the destruction of the ozone layer.
  • the main industrial sources for the formation of nitrogen protoxide are plants for the production of nitric acid and adipic acid (monomer used in the preparation of nylon 6,6 and 6,12).
  • Nitrogen protoxide is present in the emissions of adipic acid plants in considerable amounts: a typical composition comprises, in percentage by volume: 30% N 2 0, 2% C0 2 , 2.5% H 2 0, 8-12% 0 2 , 50-150 ppm NOx, remainder N 2 .
  • the emissions of nitric acid plants generally contain 300-1700 ppm of N 2 0, 100-2000 ppm of NO x , 1-4% 0 2 , and nitrogen as the remainder.
  • N 2 0 emission from nitric acid and adipic acid plants is expected to grow by approximately 16% in the period 2005-2020.
  • catalysts used for the decomposition of N 2 0 are known.
  • the main ones are constituted by noble metals supported on metallic oxides of different kinds, zeolites substituted with transition metal ions or on which metal oxides and anionic clays are supported, such as for example hydrotalcites constituted by mixed hydroxides with stratified structure, in which anions of different kinds, exchangeable or not, and water molecules are inserted between two layers.
  • Catalysts are known (US 5,705,136) which are constituted by oxides such as MnO, CuO, NiO and CoO supported on MgO, CaO, ZnO, Ti0 2 , Al 2 0 3 -ZnO, Al 2 0 3 -Ti0 2 and the like.
  • the catalysts Preferably, the catalysts contain CoO supported on MgO.
  • Structures of the type of hydrotalcite such as for example Cu 3 Mg 5 Al 2 (OH) 20 CO 3 3H 2 0, Mn 3 Mg 5 Al 2 (OH) 20 CO 3 H 2 O, are also usable.
  • the catalysts specified hereinafter have a high catalytic activity in the decomposition of N 2 0 to nitrogen and oxygen, satisfactory thermal stability up to 900 °C and the ability to keep their activity unchanged for long periods of time.
  • the stability at high temperatures is in particular provided by the catalysts when supported on alumina, which is a totally unexpected result in view of the away teaching deriving from the US application.
  • the catalysts specified hereinafter have the characteristic that they do not contain copper, an element that might have volatility problems in case of reactions conducted at high temperatures, such as for example in the operating conditions for abating of N 2 0 by-product directly in the reactor for oxidation of ammonia to nitrogen monoxide.
  • the catalysts comprise mixed oxides of cobalt, manganese and rare earth metals, which are present in the following composition expressed as percentage by weight of CoO, MnO and rare earth metal oxide, wherein the metal is present in the lowest state of valence: MnO 38-56%, CoO 22-30%, 22-32% rare earth metal oxide.
  • the preferred rare earth metal oxides are lanthanum and cerium oxides and mixtures thereof.
  • a preferred composition contains lanthanum oxide in a quantity of 25-30% by weight expressed as La 2 0 3 .
  • the mixed oxides that constitute the active components of the catalysts have the characteristic of being p-type semiconductors in which conductivity increases exponentially as the temperature rises, according to an Arrhenius-like law, and in which the charge vectors are constituted by electron vacancies.
  • the lattice oxygen takes part in the oxidation reactions.
  • the mixed oxides are used on porous inorganic supports, preferably porous oxides, such as alumina, silica-alumina, titanium dioxide, magnesium oxide.
  • Alumina preferably in the gamma form, in the form of micro spheroidal particles with a diameter of 30-80 ⁇ , is the preferred support for reactions performed particularly in a fluid bed.
  • the surface area (BET) of the catalyst supported in gamma alumina is generally comprised between 90 and 170 m 2 /g.
  • the oxides are preferably present in the support in a quantity of 10-30% by weight.
  • supports that have a definite geometric shape, such as cylindrical granules having one or more holes, preferably with three lobes, with through holes which are parallel to the axis of the granule.
  • Granule size is 3-10 mm in height and the circumference is comprised between 3 and 10 mm.
  • the preferred method consists in impregnating the support with an aqueous solution of a salt of lanthanum or cerium or other rare earth metal or mixtures thereof, followed by drying of the support and then calcination at temperatures preferably between 450 and 600 °C.
  • the support thus treated is then impregnated with a solution of a salt of manganese and cobalt, subsequently dried and calcinated at temperatures between 500 and 750 °C.
  • Any salt of the above cited metals that is soluble in water can be used; nitrates, formates and acetates are preferred.
  • the preferred impregnation method is performed dry, i.e., by using a volume of solution of the salts that is equal to, or lower than, the volume of the pores of the support.
  • the decomposition of N 2 0 is conducted at temperatures between 400 and 900 °C.
  • the higher temperatures are used as the N 2 0 content increases.
  • the preferred temperature is between 700 and 900 °C.
  • Space velocities are comprised between 3,000 and 100,000 h "1 .
  • the N 2 0 content in the mixtures varies from ppm to percentages by volume of more than 20%.
  • the catalyst used in the examples had the following composition, expressed as percentage by weight of:
  • CoO 26.3
  • the preparation was performed by impregnating gamma alumina with an aqueous solution of lanthanum nitrate La(N0 3 ) 3 .
  • the support was then dried at 110 °C and then calcinated at 450 °C.
  • the calcinated support was impregnated with an aqueous solution of manganese nitrate (Mn(N0 3 ) 2 ) and cobalt nitrate (Co(N0 3 ) 2 ) and then dried at 120-200 °C and calcinated at 700 °C.
  • a volume of solution equal to 100% of the volume of the pores of the alumina was used for impregnation.
  • the surface area of the catalyst (BET) was 160 m 2 /g and porosity was 0.40 cmVg.
  • the catalyst Prior to the test, the catalyst was ground and screened appropriately.
  • the light-off activity of the catalyst i.e., the temperature of the gaseous flow at which the catalyst decomposes 50% of the nitrogen protoxide that is present, and the temperature of total decomposition of the protoxide were selected as main criteria for evaluating the performance of the catalyst being considered.
  • results are listed in the table and relate to tests conducted at different N 2 0 concentration both on a fresh catalyst and on a catalyst aged for 3 days at 900 °C in air, so as to simulate a worsening of the reaction conditions.
  • Example 1 Example 2
  • Example 3 Example 4 conditions Fresh sample Aged sample Fresh sample Aged sample

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Organic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Environmental & Geological Engineering (AREA)
  • Biomedical Technology (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • General Chemical & Material Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • Catalysts (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
PCT/EP2011/065393 2010-09-13 2011-09-06 Catalyst for the decomposition of nitrogen protoxide Ceased WO2012034902A1 (en)

Priority Applications (9)

Application Number Priority Date Filing Date Title
US13/822,880 US8809224B2 (en) 2010-09-13 2011-09-06 Catalyst for the decomposition of nitrogen protoxide
RU2013116992/05A RU2573000C2 (ru) 2010-09-13 2011-09-06 Катализатор для разложения закиси азота
ES11752239.1T ES2666214T3 (es) 2010-09-13 2011-09-06 Catalizador para la descomposición de protóxido de nitrógeno
EP11752239.1A EP2616165B1 (en) 2010-09-13 2011-09-06 Catalyst for the decomposition of nitrogen protoxide
PL11752239T PL2616165T3 (pl) 2010-09-13 2011-09-06 Katalizator do katalitycznego rozkładu podtlenku azotu
KR1020137009320A KR101882959B1 (ko) 2010-09-13 2011-09-06 질소 초급산화물의 분해용 촉매
CN201180044013.3A CN103249468B (zh) 2010-09-13 2011-09-06 用于氧化亚氮分解的催化剂
CA2812142A CA2812142C (en) 2010-09-13 2011-09-06 Catalyst for the decomposition of nitrogen protoxide
NO11752239A NO2616165T3 (ru) 2010-09-13 2011-09-06

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
ITMI2010A001659A IT1401698B1 (it) 2010-09-13 2010-09-13 Catalizzatore per la decomposizione di protossido d'azoto.
ITMI2010A001659 2010-09-13

Publications (1)

Publication Number Publication Date
WO2012034902A1 true WO2012034902A1 (en) 2012-03-22

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PCT/EP2011/065393 Ceased WO2012034902A1 (en) 2010-09-13 2011-09-06 Catalyst for the decomposition of nitrogen protoxide

Country Status (13)

Country Link
US (1) US8809224B2 (ru)
EP (1) EP2616165B1 (ru)
KR (1) KR101882959B1 (ru)
CN (1) CN103249468B (ru)
CA (1) CA2812142C (ru)
ES (1) ES2666214T3 (ru)
HU (1) HUE036900T2 (ru)
IT (1) IT1401698B1 (ru)
NO (1) NO2616165T3 (ru)
PL (1) PL2616165T3 (ru)
PT (1) PT2616165T (ru)
RU (1) RU2573000C2 (ru)
WO (1) WO2012034902A1 (ru)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103586040B (zh) * 2013-11-13 2017-02-08 刘崇莲 一种处理n2o的催化剂及其制备工艺
CN104437499A (zh) * 2014-10-31 2015-03-25 兰州天越环保科技有限公司 一种用于分解氧化亚氮的催化剂及其制备方法
CN106944048A (zh) * 2017-03-08 2017-07-14 昆明南铂环保科技有限公司 氧化亚氮转化催化剂

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB2059934A (en) * 1978-10-17 1981-04-29 Kuraray Co System for treating waste anaesthetic gas
DE19506659C1 (de) * 1995-02-25 1996-08-08 Leuna Katalysatoren Gmbh Kobalt-, Lanthan- und Lanthaniden-Oxide enthaltender Katalysator mit vorwiegend Perowskit-Struktur und Verfahren zu seiner Herstellung
US5705136A (en) 1995-11-13 1998-01-06 University Of Florida Research Foundation, Inc. Catalyzed decomposition of nitrogen oxides on metal oxide supports
US20040179986A1 (en) 1998-09-09 2004-09-16 Porzellanwerk Kloster Veilsdorf Gmbh Ceramic catalyst for the selective decomposition of N2O and method for making same
WO2004096703A2 (en) * 2003-04-29 2004-11-11 Johnson Matthey Plc Ammonia oxidation process
JP2005095786A (ja) * 2003-09-25 2005-04-14 Nippon Shokubai Co Ltd アンモニア含有排ガスおよびアンモニア含有排水の浄化方法
WO2008090450A1 (en) * 2007-01-23 2008-07-31 Sued-Chemie Catalysts Italia S.R.L. Process for catalytic decomposition of nitrogen protoxide
EP2202201A1 (en) * 2008-12-23 2010-06-30 SÜD-CHEMIE CATALYSTS ITALIA S.r.l. Ammonia oxidation catalysts

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
SU1766497A1 (ru) * 1991-01-11 1992-10-07 Омский Научно-Технический Филиал Республиканского Инженерно-Технического Центра Со Ан Ссср Катализатор дл очистки отход щих газов от окиси углерода, углеводородов и окислов азота

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB2059934A (en) * 1978-10-17 1981-04-29 Kuraray Co System for treating waste anaesthetic gas
DE19506659C1 (de) * 1995-02-25 1996-08-08 Leuna Katalysatoren Gmbh Kobalt-, Lanthan- und Lanthaniden-Oxide enthaltender Katalysator mit vorwiegend Perowskit-Struktur und Verfahren zu seiner Herstellung
US5705136A (en) 1995-11-13 1998-01-06 University Of Florida Research Foundation, Inc. Catalyzed decomposition of nitrogen oxides on metal oxide supports
US20040179986A1 (en) 1998-09-09 2004-09-16 Porzellanwerk Kloster Veilsdorf Gmbh Ceramic catalyst for the selective decomposition of N2O and method for making same
WO2004096703A2 (en) * 2003-04-29 2004-11-11 Johnson Matthey Plc Ammonia oxidation process
JP2005095786A (ja) * 2003-09-25 2005-04-14 Nippon Shokubai Co Ltd アンモニア含有排ガスおよびアンモニア含有排水の浄化方法
WO2008090450A1 (en) * 2007-01-23 2008-07-31 Sued-Chemie Catalysts Italia S.R.L. Process for catalytic decomposition of nitrogen protoxide
EP2202201A1 (en) * 2008-12-23 2010-06-30 SÜD-CHEMIE CATALYSTS ITALIA S.r.l. Ammonia oxidation catalysts

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
KARASKOVA K ET AL: "Effect of promoters in Co-Mn-Al mixed oxide catalyst on N2O decomposition", CHEMICAL ENGINEERING JOURNAL, ELSEVIER SEQUOIA, LAUSANNE, CH, vol. 160, no. 2, 1 June 2010 (2010-06-01), pages 480 - 487, XP027051648, ISSN: 1385-8947, [retrieved on 20100514] *
OBALOVA L ET AL: "Effect of potassium in calcined Co-Mn-Al layered double hydroxide on the catalytic decomposition of N2O", APPLIED CATALYSIS B: ENVIRONMENTAL, ELSEVIER, vol. 90, no. 1-2, 25 July 2009 (2009-07-25), pages 132 - 140, XP026139922, ISSN: 0926-3373, [retrieved on 20090313], DOI: DOI:10.1016/J.APCATB.2009.03.002 *
RUSSO ET AL: "N2O catalytic decomposition over various spinel-type oxides", CATALYSIS TODAY, ELSEVIER, NL, vol. 119, no. 1-4, 29 October 2006 (2006-10-29), pages 228 - 232, XP005839423, ISSN: 0920-5861, DOI: DOI:10.1016/J.CATTOD.2006.08.012 *
XUE ET AL: "Catalytic decomposition of N2O over CeO2 promoted Co3O4 spinel catalyst", APPLIED CATALYSIS B: ENVIRONMENTAL, ELSEVIER, vol. 75, no. 3-4, 5 September 2007 (2007-09-05), pages 167 - 174, XP022230849, ISSN: 0926-3373, DOI: DOI:10.1016/J.APCATB.2007.04.013 *

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Publication number Publication date
RU2573000C2 (ru) 2016-01-20
US20130172178A1 (en) 2013-07-04
HUE036900T2 (hu) 2018-08-28
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EP2616165B1 (en) 2018-01-17
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CN103249468A (zh) 2013-08-14
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ITMI20101659A1 (it) 2012-03-14
CA2812142A1 (en) 2012-03-22
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US8809224B2 (en) 2014-08-19
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